FLasher_reference.Rmd
This document focuses on the details of the projection methods of the FLasher package. These are implemented in C++ using RCpp amd CppAD. It is not intended to teach people how to use FLasher but to act as a reference for the package and describe how projections using Flasher are carried out. Particular attention is paid to the operatingModel class, and how the components of an operatingModel object (FLFisheries, fwdBiols etc.) interact.
In FLasher, an operating model is made up of the fisheries that perform fishing activity and the biological stocks. Operating models are represented by the operatingModel class which make up the heart of the projection.
ADD DIAGRAM
The biological stocks (Biols) in the operating model are stored as an object of class fwdBiols. This is a list of the Biols, each stored as an fwdBiol object (analagous to the FLBiol class in R). Each fwdBiol contains the abundance and life history information of the biological stock through time, such as mean weights at age, maturity etc. The stock recruitment relationship is also stored in the fwdBiol here, as an object of class fwdSR.
The Fisheries are represented by an object of class FLFisheries. This is a list of FLFishery objects, each of which represents an individual Fishery. An FLFishery is a fleet (set of vessels) that has the same metier or gear type, e.g. beam trawlers or long lines. A Fishery is made up of a series of Catches, each one is represented by an object of class FLCatch. Each FLCatch object represents the catch from a fish stock (usually from a single Biol - mixing catches from more than one Biol is a special case where catches from multiple biological stocks are represented as catches from a single Biol). A Fishery may have only a single Catch, i.e. it only catches from one Biol. Multiple Catches inside a Fishery cannot catch from the same Biol, i.e. a Fishery can only catch once from a biological stock.
The FLCatch object contains the landing and discard numbers and weights along with the selectivity and catchability parameters. They interact with the biological stocks by imposing fishing mortality. Fishing effort is defined at the level of the Fishery so that all Catches inside the same Fishery have the same effort.
For example, if a fishery catches plaice and sole, there would be two FLCatch objects: one for plaice and one for sole. Each one would have different landing and discards weights, selectivity and catchability. However, they have the effort as fishing effort is defined at the fishery level not the catch level.
The third main member of the operatingModel class is an fwdControl object. This specifies that timesteps, target types and values of the projection. It also describes how the Fisheries, Catches and Biols interact with each other through the FCB matrix.
The simplest operating model is one which has a single fishery with a single catch fishing a single biological stock.
DIAGRAM
A mixed fishery is one with technical interactions (i.e. a stock may be caught by more than fishery or type of gear). Simple example: two fisheries on one stock.
DIAGRAM
A projection can either be annual or seasonal. The number of seasons in a year is up to the user. Each timestep of a projection, whether season or year, is handled independently.
The projection is driven by the effort in the FLFisheries at that timestep (i.e. the effort in each FLFishery in the operating model). The projection is split into two stages: projecting the fisheries in a timestep (to calculate the catches in that timestep based on the effort and biological abundance in that timestep) and projecting the biology (to calculate the biological abundance in the next timestep based on the fishing mortality in the previous timestep).
In both of these steps fishing mortality is the key metric that drives removals resulting in the catches and changes in the biological stock abundance.
Fishing effort drives the catches and biological stock abundance through fishing mortality. As such, it is a key metric of the model.
Fishing mortality (F) is an age-structured metric that represents the impact of fishing on the stock. Inside FLasher it is the result of the interaction between an FLCatch and an fwdBiol object.
The fishing mortality imposed on a Biol from a single Catch is known as the partial fishing mortality. As mentioned above, a Biol can be fished by multiple Catches.
The partial fishing mortality is calculated as:
\(pF_{a,c,b} = \alpha_{c} Sel_{a,c} E_{f}\)
where \(a\) is age, \(b\) the Biol, \(c\) the Catch, \(f\) is the Fishery that contains the Catch, \(pF\) is the partial fishing mortality, \(\alpha\) is the catchability scaling parameter, \(Sel\) is the gear selectivity and \(E\) is the fishing effort. \(\alpha\) can be set so that a particular effort and selectivity result in the desired F. Note that fishing effort is set at the Fishery level and each Catch of an Fishery has the same fishing effort.
The total fishing mortality imposed on a stock from all the FLCatches
that fish it is the sum of the partial fishing mortalities:
\(F_{a,b} = pF_{a,b,c1} + pF_{a,b,c2} + ...\)
where \(cx\) is the index of the Catches fishing the stock, \(F\) is the total fishing mortality and \(pF\) is the partial fishing mortality.
Internally, the catchability parameter, \(\alpha\), is stored in the FLCatch object as an FLQuant. This means that it can vary over the year, unit, season, area and iter dimension (the first dimension is not used). For example, \(\alpha\) could increase over time to represent technological creep. The value of \(\alpha\) is recycled over the dimensions over which it does not change i.e. if \(\alpha\) does not change over any dimension then it is only necessary to set a single value in the FLQuant.
The selectivity is also stored in the FLCatch object as an age-structured FLQuant. This means that it can vary over the year, unit, season, area and iter dimension. The selectivity should be scaled between 0 and 1. The selectivity FLQuant needs to be the correct dimensions for the whole projection, i.e. there is no recycling apart from the iter dimension.
Effort is stored at the FLFishery level so that the same effort is used for all the FLCatch objects in the Fishery. It is stored as an FLQuant but the first dimension is not used. Additionally, it has no unit structure. The effort FLQuant needs to have the same year and season dimensions as the projection, i.e. there is no recycling apart from the iter dimension.
In each time step of the projection, the landings and discards numbers are updated in the FLCatches of the FLFishery objects. In FLasher, the projection is carried out using the operatingModel project_fisheries() method. Catch numbers at age in each time step are calculated for each of the FLCatch objects inside each of the FLFishery using the Baranov equation (REF).
A biological stock may be fished by more than one FLCatch. The catch of one FLCatch from a biological stock is known as the partial catch. The total catch of a biological stock equals the sum of the partial catches from that stock.
\(C_{a,b} = pC_{a,b,c1} + pC_{a,b,c2} + ...\)
where \(cx\) the Catch, \(C\) is the total catch and \(pC\) is the partial catch from each Catch. Where a stock is only fished by a single Catch, the partial catch is equal to the total catch.
The partial catch of a Catch from a biological stock is given as:
\(pC_{a,b,c} = (pF_{a,b,c} / Z_{a,b}) * (1 - exp(-Z_{a,b})) * N_{a,b}\)
where \(a\) is age, \(b\) the Biol, \(c\) the Catch, \(pC\) is the partial catch, \(pF\) is the partial fishing mortality, \(Z\) is the total mortality of the biological stock being fished (total fishing mortality of the stock plus natural mortality) and \(N\) is abundance of the biological stock being fished.
The total mortality is given as:
\(Z_{a,b} = F_{a,b} + m_{a,b}\)
where \(m\) is the natural mortality of the biological stock.
\(N\) and \(m\) are stored in the corresponding fwdBiol object.
Landings and discards numbers are calculated by splitting the catch numbers using the discard ratio. When the FLFishery is created in C++ from the R objects, the discard ratio is calculated from the existing landings and discards numbers in the R-based object, i.e. the future discard ratio can be set up by entering the appropriate values in the future landings and discards numbers. These values are then written over with the actual landings and discards during the projection.
\(DR_{a,c} = D_{a,c} / (D_{a,c} + L_{a,c})\)
where \(DR\) is the discard rate, \(D\) is the discard numbers and \(L\) is the landings numbers.
In the operatinModel, the discard ratio is stored as an FLQuant of the FLCatch object. During a projection it is used to split the calculated catch numbers into landings and discards:
\(L_{a,c} = pC_{a,c} * (1 - DR_{a,c})\) \(D_{a,c} = pC_{a,c} * DR_{a,c}\)
There is a special case where a single Catch may catch from more than one Biol (for example, where two biological stocks are considered to be a single stock by the management regime). In this special case the sum of the landings and discard numbers from each stock are in the FLCatch.
There is a difference between FLasher and FLash concerning the calculation of total catch biomass. In FLasher and FLash catch numbers at age are the sum of the landing and discards numbers at age. In FLash the mean catch weights at age are fixed in advance in using the catch.wt slot. In FLasher the mean catch weights at age are calculated using the landings and discards numbers and weights at age. This means the that mean catch weights at age in FLasher are not fixed in advance but will change according to the projected landings and discards numbers. The result is that the mean catch weights at age will differ between FLash and FLasher. This difference is most noticeable when a total catch is set as a target. Both FLash and FLasher will hit the same total catch weight target but because the mean catch weights at age are different, the catch numbers at age will be different.
The biological stocks are projected one timestep at a time by the project_biols() method. The method calculates the survivors from the previous timestep and places them in the current timestep. Recruitment in the current timestep is also calculated.
The Biols are processed one at a time (the order in which they appear in the biols
member). The Biols are independent of each other and there is no interaction between them.
The projection sequence is:
The abundances in a fwdBiol class represent the abundances at the start of a timestep, i.e. before any fishing or natural mortality occurs. The survivors at the end of a timestep, \(S\), at age, \(a\), at the end of a timestep (given by year, \(y\) and season, \(s\)) are calculated as:
\(S_{a,y,s} = N_{a,y,s} exp(-Z_{a,y,s})\)
where \(N\) is the population abundance at the start of the timestep.
The survivors are put into the abundances in the next timestep. The age group that survivors are placed in depends on the timestep and the timing of recruitment. The recruitment is always added to the first age group of the stock in the timestep in which it occurred. As the projection progresses, the survivors at the end of a timestep are placed in the same age group in the next timestep until they are a year older. When they are a year older, the survivors are placed in the next age group.
For example, say we have a projection with 4 seasons to a year and the stock only recruits once a year in season 3. Recruits enter the first age group in season 3. In season 4, the survivors from season 3 are placed in the same age group (e.g. the recruits from season 3 are moved to the first age group in season 4, less those that died). The same thing happens in the following year in seasons 1 and 2. In season 3 of the following year (the recruitment season) the survivors are placed in the next age group, i.e. the individuals are now a year older.
ILLUSTRATE EXAMPLE
Recruitment is one of the most important biological processes as it drives the dynamics and productivity of the stock. It is also a source of great uncertainty and can be strongly affected by external drivers such as environmental conditions.
In Flasher, calculating recruitment has two main stages:
A Biol may spawn and recruit more than one time in a year, e.g. it can recruit in multiple seasons, but recruitment can only happen once in a timestep. This means that if there are multiple recruitment events in a year, the model must be seasonal. When a stock recruits more than one time in year, the resulting recruitment from each event is placed into a different unit of the stock. For example, if the stock recruits twice a year, then the stock must have at least two units. This is because life-history characteristics, such as the mean weights at age, will be different for individuals that are recruited at different times of the year. A unit can only recruit once per year.
The recruitment of each unit of a fwdBiol is calculated separately and may have different stock recruitment parameters. However, the SRP that produces the recruitment is the total SRP across all units, i.e. the SRP of each individual unit is not considered, only the total.
The abundance in an fwdBiol is the abundance at the start of the timestep. The calculated recruitment is inserted into the abundance in the same timestep meaning that we calculate recruitment at the start of the timestep. It is inserted into the first age group of the biol.
The final step in calculating recruitment is the application of deviances. This is an additional multiplier applied to the calculated recruitment. The deviances can be used to introduce further uncertainty on the recruitment.
The deviances are stored as an FLQuant. Internally, this must have the same time dimensions as the model. However, the R method fwd() accepts deviances just for the projection years. The first dimension of the deviances is length 1.
The SRP represents the total recruitment potential of the Biol at the time of spawning.
As mentioned above, a biological stock may have multiple units from multiple recruitment events in a year. Although the SRP of each unit can be calculated individually, the SRP that is used to calculate recruitment is the total SRP of all units. The total SRP of a fwdBiol in a timestep is given by the sum of the SRPs of each unit.
\(SRP_{y,s} = \sum_{u=1}^{U}SRP_{y,s,u}\)
where \(u\) is the unit and \(U\) is the total number of units.
There are several possible measures of SRP, e.g. spawning stock biomass (SSB), egg production etc. At the moment, Flasher only uses SSB. Alternative measures will be included in the future.
The SSB of a unit in a timestep is given by:
\(SSB_{y,s,u} = \sum_{a=1}^{A} N_{a,y,s,u} Mat_{a,y,s,u} Wt_{a,y,s,u} exp(-Zprespwn_{a,y,s,u})\)
Where \(A\) is the number of ages in the stock, \(Mat\) is the proportion mature (the mat
slot of an FLBiol), \(Wt\) is the mean weights at age (the wt
slot of an FLBiol) and \(Zprespwn\) is the amount of mortality (fishing and natural) experienced by the stock before spawning occurs in that timestep (see next section).
SRP is the spawning potential of the Biol at the time of spawning. This means that timing is very important in the calculation of the SRP.
The timing of spawning is handled by the spwn slot of the FLBiol (in C++ it is the spwn member of the fwdBiol class). spwn is an FLQuant with a length of one in the first dimension (i.e. there is no age structure). It takes a value of 0 - 1 which describes the point in the timestep when spawning happens. For example, a value of 0 means that spawning happens at the start of the timestep, a value of 0.5 is halfway through the timestep, a value of 1 is the end of the timestep and so on. Importantly, a value of NA means that there is no spawning in that timestep and the calculated SRP of that unit in that timestep is 0 (not NA).
When a Biol has multiple units, it is technically possible for different units to spawn at different times. However, this is pretty unlikely and generally, all units spawn at the same time. When there are multiple units, it is important that the resulting recruitment is placed into the correct unit (see below).
In FLasher, the abundances in a timestep are the abundances at the start of that timestep. When calculating SRP in a timestep, it is necessary to calculate the abundance at the time of spawning. With a seasonal model spawning will probably happen at the start of a timestep (i.e. spwn = 0). However, with an annual model this may not be the case. If spawning happens part way through a timestep, by the time the population spawns it will have experienced natural mortality and possibly fishing mortality. This means that the abundance at the time of spawning will be lower than at the start of the timestep. Consequently, we need to calculate the population abundance at the time of spawning, not at the start of the timestep. For example, if we have an annual model and spawning occurs midway through the year, we need to calculate the abundance midway through the year, after some of the natural and fishing mortality have taken place.
In the calculation of SRP the decrease in abundance by the time of spawning is handled by \(Zprespwn\). This is the sum of the amount of fishing and natural mortality experienced by the stock before spawning, \(Fprespwn\) and \(Mprespwn\) respectively:
\(Zprespwn = Fprespwn + Mprespwn\)
\(Fprespwn\) needs to consider the timing of spawning and the timing of the fishing period within each timestep. The timing of fishing is controlled by the hperiod slot of an FLFishery (each FLCatch of a fishery has the same timing). hperiod is an FLQuant with length two in the first dimension. It is not age structured and the first dimension has names start and end to hold the start and end times of the fishing period in that timestep. The values are between 0 and 1 in the same way as the spwn slot of the FLBiol. A value of NA in start means no fishing in that timestep (alternatively, the effort can be set to 0).
A Biol can be fished by more than one fishery. \(Fprespwn\) is calculated for each Fishery that fishes the Biol and then summed. For each Fishery that fishes the Biol it is necessary to calculate how much fishing has occured before spawning in a timestep. If fishing starts after spawning (\(start > spwn\)) then the population abundance at spawning time is unaffected by fishing from that fishery. If fishing finishes before spawning (\(end < spwn\)) then the population abundance at spawning is reduced by the total fishing mortality from that Fishery. If spwn falls between start and end then it is necessary to calulate how much fishing has occured before spawning. This calculation is handled by the f_prop_spwn() method (a member of the operatingModel class). This calculates the proportion of the fishing mortality from each Fishery that happens before spawning, \(Fpropmult\). The fishing mortality from a Fishery that is applied before spawning is then the total fishing mortality from that Fishery, in that timestep, multiplied by the proportion:
\(Fprespwn = F * Fpropmult\)
Natural mortality is assumed to happen continuously throughout the year so the amount of natural mortality before spawning is:
\(Mprespwn = M * spwn\)
Spawning results in recruitment at age 0. However, the first age of the model is not necessarily 0. Therefore, when calculating recruitment it is necessary to calculate the SRP in the appropriate timestep. The timelag between spawning and recruitment depends on the first age of the stock and whether the model is seasonal:
For example, if the first age of the Biol is 2, then the recruitment is a function of the SRP two years ago (2 timesteps for an annual model).
In Flasher the method srp_timelag() (a member of the fwdBiol class) calculates the lag between the current timestep and the timestep of the corresponding SRP.
Recruitment is calculated using the total SRP of the Biol. The calculation uses the SRP and the stock recruitment parameters. The SRR parameters are used to calculate the recruitment in that timestep, i.e. they are related to the timing of recruitment, not spawning.
The SRR parameters are stored as an FLQuant in the fwdSR member of the fwdBiol. The parameters are stored in the first dimension and can be disaggregated over the other dimensions. Recruitment for each unit is calculated separately. Recruitment for a unit is only calculated if the first SRR parameter of that unit in that timestep is not NA. If the first parameter is NA in that timestep then recruitment is not calculated, even if the corresponding SRP is greater than 0. If the first parameter is not NA, recruitment is calculated, even if the corresponding SRP is 0. This means that the presence or absence of NAs in the SRR parameters determines in which timesteps recruitment happens.
During a projection it is important to keep track of when recruitment occurs because it determines where survivors are placed during the projection. In the timesteps when recruitment occurs, the survivors from the previous timestep are placed in the next age group, i.e. they are one year older. In the timesteps when recruitment does not occur, the survivors from the previous timestep are placed in the same age group. For example, if the model has 4 seasons and recruitment happens in season 4, the survivors from season 2 to 3 are placed in the same age group as they were in season 2 but survivors from season 3 to 4 are placed in the next age group.
The dimensions of the SRR parameter FLQuant do not need to match the dimension of the fwdBiol
as the SRR parameters are recycled where necessary. For example, if the model is annual and the SRR parameters are the same every year, then the SRR parameters do not need to be disaggregated by year. If there is a trend in the SRR parameters, then you can set different parameter values in every year. The recycling works over all dimensions (expect the first dimension) including iterations.
If a dimension is disaggregated it should be the same size as the rest of the model, otherwise only the first value is used. For example, if the model has 50 years and the SRR parameters have only 10 years, only the first year of the SRR parameters will be used.
Due to the recycling of the SRR parameters, care must be taken to set up the SRR parameters when the model is seasonal. If the first SRR parameter in a timestep is not NA, the recruitment will be calculated. This means that if you have a seasonal model that does not recruit in every season, the SRR parameters need to be disaggregated by season. If they are not (i.e. the SRR parameters only have one season) then the parameters will be recycled over all seasons. This means that recruitment will be calculated in each season and the result placed into a different unit.
Similarly, if there are multiple recruitment events in a year, the SRR parameters need to be disaggregated by unit. If they are not, the units will be assumed to be recruiting at the same time which is not correct.
The model can become complicated when the stock has multiple recruitment events. This is explored in more detail here.
Within a year a stock may recruit multiple times. To ensure that the life history parameters of an individual (such as mean weight at age) are consistent with its recruitment season, it is necessary to account for the individuals from each recruitment event separately. For example, consider a stock that recruits in seasons 1 and 3. The recruits from each event will be placed in the first age group. However, the individuals that were recruited in season 1 will be two seasons older than those that are recruited in season 3. Consequently, their mean weight at age and other metrics will be different. We have to keep track of the individuals recruited in season 1 and season 3 separately. To do this we use the unit dimension.
The unit dimension is used to store information on individuals from different recruitment events. The individuals that are produced in each recruitment event in a year must be stored in a different unit. A Biol with multiple recruitment events must have a unit for each recruitment event and must also be seasonal (recruitment can only happen once in a timestep so multiple recruitment events implies multiple timesteps in a year).
As mentioned above, due to the recycling of SRR parameters, it is necessary to disaggregate the SRR parameters by unit and season. The units may have the same SRR parameters but the timing of recruitment will be different for each unit. If the SRR parameters were not disaggregated by unit and season then we would know in which season each unit recruits. The SRR parameters should therefore be NA for the units in the timesteps that they do not recruit. If not, the same SRR parameters will be used for all units, meaning that the units will recruit at the same time. This is not supposed to happen.
An enumerated type, fwdControlTargetType is used to store the target type. This is defined in the fwdControl.h header file. At the moment, targets cannot be set at the age or unit level. The targets are aggregated over all units and ages.
It is possible for the control target to have iterations. If there are no iterations, but the model does have iterations (e.g. in the biological abundance), then the same control target value is used for all iterations.
Different target types require different combinations of Fishery, Catch and Biol to be specifed in the control object. The following table describes the requirements:
Target type | Fishery | Catch | Biol | Notes |
---|---|---|---|---|
Catch | X | X | ||
X | Not possible if Biol is caught by a Catch that also catches another Biol | |||
Landings | X | X | ||
X | Not possible if Biol is caught by a Catch that also catches another Biol | |||
Discards | X | X | ||
X | Not possible if Biol is caught by a Catch that also catches another Biol | |||
F | X | Total F on a biol | ||
X | X | X | Partial F of a Fishery and Catch on a Biol | |
Effort | X | |||
Revenue | X | Total revenue of the fishery | ||
X | X | Revenue from a single Catch | ||
SSB | X | Various SSB targets are available (see below) | ||
Biomass | X | Various biomass targets are available (see below) | ||
SRP | X |
With biologically based targets we have to be careful with the timing:
at the end of the timestep
, i.e. the survivors after all mortality (fishing and natural) has stopped.next
time step is returned. Similarly, if there is no spawning in that time step, the SSB or biomass at the time of spawning in the next
time step is returned (unless there is also no spawning in the next time step in which case an error occurs’. This behaviour is a bit dangerous because if we are trying to get the SSB or biomass in the next time step and fishing in the next time step happens before spawning, the SSB or biomass will be affected by the fishing effort in the current time step and
the next time step (which is not solved for). Due to the weird nature of this target type it is better to only use if for annual models.Note that as SRP
target is the SRP at the time of spawning, if the fishing periods starts after spawning then the fishing mortality in that timestep will have no impact on the SRP. The solver will fail in this case.
Fbar targets are set at either:
In the first case, the Biol number must be specified in the control object. In the second case, the Fishery, Catch and Biol number must be specified in the control object (fwd() may make an internal attempt at filling this in, for example when the projection object is an FLStock which has one Fishery / Catch and Biol. However, it will be safer for the user to specify clearly what they want).
When setting an Fbar target it is necessary to set the age range over which to calculate it. The age range is set using the minAge and maxAge columns in the control object. This is done automatically when the projection object is an FLStock by taking the information from the range slot.
Fbar targets have a single unit, i.e. when the objects have multiple units, the Fbar is the Fbar of the combined unit. This means that it is not possible to set an Fbar target for a particular unit.
This presents some problems as calculating the combined Fbar of an object with multiple units is more complicated than an object with a single unit. Although it is possible to calculate the F of each unit, there is no easy way of combining these into a single unit i.e. you cannot just take the mean across the units. Instead, FLasher attempts to calculate the unit-combined F by using the unit-combined catch numbers, abundances and survivors: First, the unit combined \(z\) is calculated using:
\(combined_z = log(combined_n / combined_survivors)\)
Then the unit combined \(f\) is calculated using:
\(combined_f = (combined_catch * combined_z) / (combined_n * (1 - exp(-combined_z)))\)
or, as \(survivors = N exp(-combined_z)\):
\(combined_f = (combined_catch * log(combined_n / combined_survivors)) / (combined_n - combined_survivors)\)
This method is implemented as get_f_nunit() (called either with a Biol for the total F, or with a Fishery, Catch and Biol for the partial F). When evaluating Fbar, the get_f_nunit() method is only called when multiple units are present. When single units are present, the normal get_f() methods are used.
Calculating the unit combined F requires the unit combined catch numbers. For example, when calculating the combined F of a Biol, you need the combined total catch from that Biol, and when calculating the combined partial F of a Fishery, Catch and Biol, you need the combined partial catch of that Fishery and Catch from that Biol.
However, it is currently not possible to access the catch from a Biol when the Catch that fishes that Biol also fishes on other Biols (it is not a common case). This is because it is not possible to attribute the total catch of that Catch to a particular Biol. The result is that it is not currently possible to calculate the unit combined F or unit combined Fbar for a Biol, partial or otherwise, in this situation. If this is attempted, there is an error message (SHOW EXAMPLE). Although, it is of course possible to calculate these catches, the current implementation of FLasher simply takes the existing catch numbers from the Catches in the operating model. They are not calculated ‘live’ each time they are asked for.
This section describes how the targets are evaluated in FLasher. It is a description of the internal workings of FLasher and is, therefore, of limited interest to most users.
To solve the projection, FLasher attempts to find the fishing effort values in the appropriate timestep to hit the desired target:
\(error = target - \hat{target}\)
Where \(target\) is the target (what we want, calculated from the the fwdControl object), \(\hat{target}\) is the state of the operating model at a given level of fishing effort (where we are) and \(error\) is the difference between the two. FLasher attempts to find the fishing efforts so that \(\hat{target}\) results in \(error\) equalling 0.
This is handled by three operatingModel class methods:
get_target_value() and get_target_value_hat() are used to get \(target\) and \(\hat{target}\) respectively. Both of these methods use the eval_om method.
This method takes the desired target value from the fwdControl object. It is called to calculate what we want.
If the target is a minimum or maximum constraint then it is necessary to evaluate the current value of the target type in the operating model, given the current fishing effort, to see if the constraints are active. The desired target value is updated as a result. For example, if there is a maximum catch target and current catch value in the operating model is greater than the maximum catch target, the target value is set to the maximum target. If the current catch value is less than the maximum catch target, then the target value is set to the current catch value i.e. there is no need to constrain the effort as the constraint has not been breached.
The evaluation of the current value of the target type in the operating model is carried out by calling the get_target_value_hat() method.
The returned value is a vector of values. The values in the vector are the target values for each iteration in the model. There is no other structure in the returned value, e.g. there is no age structure (although, conceivably, a target could be set a for a single age).
This method does use the target type. It is only concerned with values. When there is a target constraint and the target type is needed, it is handled by the get_target_value_hat() method.
This method calculates the current state of a target in the operating model, i.e. it finds out where we are given the current level of fishing effort. The method interrogates the fwdControl object and retrieves the appropriate Fishery, Catch and Biol number. It also sets up the indices ranges (year, season etc.) over which to evaluate the target type.
The evaluation is carried out by the method eval_om().
If the target is a relative target, it evaluates the absolute both values and then calculates the ratio.